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Global metabolic impacts of recent climate warming

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Abstract

Documented shifts in geographical ranges, seasonal phenology, community interactions, genetics and extinctions have been attributed to recent global warming. Many such biotic shifts have been detected at mid- to high latitudes in the Northern Hemisphere-a latitudinal pattern that is expected because warming is fastest in these regions. In contrast, shifts in tropical regions are expected to be less marked because warming is less pronounced there. However, biotic impacts of warming are mediated through physiology, and metabolic rate, which is a fundamental measure of physiological activity and ecological impact, increases exponentially rather than linearly with temperature in ectotherms. Therefore, tropical ectotherms (with warm baseline temperatures) should experience larger absolute shifts in metabolic rate than the magnitude of tropical temperature change itself would suggest, but the impact of climate warming on metabolic rate has never been quantified on a global scale. Here we show that estimated changes in terrestrial metabolic rates in the tropics are large, are equivalent in magnitude to those in the north temperate-zone regions, and are in fact far greater than those in the Arctic, even though tropical temperature change has been relatively small. Because of temperature's nonlinear effects on metabolism, tropical organisms, which constitute much of Earth's biodiversity, should be profoundly affected by recent and projected climate warming.
LETTER doi:10.1038/nature09407
Global metabolic impacts of recent climate warming
Michael E. Dillon
1
, George Wang
2
{& Raymond B. Huey
2
Documented shifts in geographical ranges
1,2
, seasonal phenology
3,4
,
community interactions
5
, genetics
3,6
and extinctions
7
have been
attributed to recent global warming
8–10
. Many such biotic shifts
have been detected at mid- to high latitudes in the Northern
Hemisphere
4,9,10
—a latitudinal pattern that is expected
4,8,10,11
because warming is fastest in these regions
8
. In contrast, shifts in
tropical regions are expected tobe less marked
4,8,10,11
because warm-
ing is less pronounced there
8
. However, biotic impacts of warming
are mediated through physiology, and metabolic rate, which is a
fundamental measure of physiological activity and ecological
impact, increases exponentially rather than linearly with tem-
perature in ectotherms
12
. Therefore, tropical ectotherms (with
warm baseline temperatures) should experience larger absolute
shifts in metabolic rate than the magnitude of tropical temperature
change itself would suggest, but the impact of climate warming on
metabolic rate has never been quantified on a global scale. Here we
show that estimated changes in terrestrial metabolic rates in the
tropics are large, are equivalent in magnitude to those in the north
temperate-zone regions, and are in fact far greater than those in
the Arctic, even though tropical temperature change has been rela-
tively small. Because of temperature’s nonlinear effects on meta-
bolism, tropical organisms, which constitute much of Earth’s
biodiversity, should be profoundly affected by recent and projected
climate warming
2,13,14
.
Global warming is probably having profound and diverse effects on
organisms
1
11
. Organisms living at mid- to high latitudes in the
Northern Hemisphere are predicted to be the most affected by climate
warming
4,8,10,11
, because temperatures have risen most rapidly there
8
.
Indeed, the vast majority of biotic impacts of warming have been
documented in this region, but few studies have yet searched for
impacts in other areas, especially the tropics
2,4,8,10,13,14
. One way to
circumvent this geographical sampling bias is to use temperature data
with broad geographical coverage to predict global patterns of physio-
logical responses to observed temperature change
13
. Metabolic rate is a
heuristic metric here because it is a fundamental physiological index of
an organism’s energetic and material needs, its processing capacity and
its ecological impact
12
.
Metabolic rates of ectotherms depend principally on body mass (m)
and body temperature (T), as described by a fundamental equation
12
:
B(m,T) 5b
0
m
3/4
e
2E/kT
(1)
where Bis metabolic rate, b
0
is an empirically derived and taxon-
specific normalization constant, mis body mass, Eis the average activation
energy for biochemical reactions of metabolism, Tis body temperature (in
Kelvin), and kis the Boltzmann constant. When standardized for mass,
this equation enables metabolic comparisons among different sized
organisms
12
. These mass-normalized metabolic rates are proportional
to the ‘Boltzmann factor’ (e
2E/kT
;thefamiliar‘Q
10
’ effect in physiology
is an approximation of the Boltzmann factor)
15
.
Although the thermodynamic and statistical validity of equation (1)
is debated
16–18
, it provides a useful approximationof metabolic rates
12,15
for exploratory macrophysiological investigations
16,19
. In the context of
climate warming, it predicts that metabolism will shift more in res-
ponse to a unit change in temperature at high temperature than at low
temperature
15
, at least over biologically common and non-stressful
temperatures (,0uCto,40 uC; see Methods)
12
.
To estimate geographical patterns of warming-induced changes in
metabolic rates of terrestrial ectotherms, we compiled high-frequency
temperature data for the period of 1961 to 2009 for 3,186 weather
stations across the world (,500 million temperature measurements;
Methods and Supplementary Fig. 1)
20
. We derived average values of
E(0.69) and of b
0
(23.66) from empirical estimates for diverse
ectotherms (Supplementary Table 1)
12
. We substituted these ‘average
ectotherm’ values into equation (1) to estimate mass-normalized meta-
bolic rates (Bm
23/4
) from global temperature data. Because metabolic
rate varies nonlinearly with temperature, calculating mean metabolic
rates from mean temperatures is inappropriate (the ‘fallacy of the
averages’; see Methods and Supplementary Fig. 2)
15
. Therefore we
estimated metabolic rate for each temperature measurement and sub-
sequently determined average temperature and average metabolic rate
for each station during the Intergovernmental Panel on Climate
Change (IPCC) standard reference period (1961–1990) and for all
five-year intervals from 1980 to 2009. To account for non-uniform
distribution of stations and to enable comparisons among latitudinal
regions, we determined averages for all stations within 5ulatitude by 5u
longitude grid cells and then area-corrected grid-cell means and standard
errors of temperature measurements and metabolic rate estimates for
each region (Methods).
Temperature changes since 1980 in this data set are consistent with
recent findings
8
: temperatures rose fastest in the Arctic, somewhat less
quicklyin the north temperatezones, and more slowlyin the tropics, but
remained essentially unchanged in the south temperate zone (Fig. 1a).
Predicted absolute changes in metabolic rates show a markedly
different pattern: metabolic rates increased most quickly in the tropics
and north temperate zones, and less so in the Arctic (Fig. 1b). In fact,
the latitudinal ordering of changes in temperature since 1980 fails to
predict the latitudinal ordering of changes in metabolic rate (P50.68),
even when a powerful ordered-heterogeneity test is used
21
. The pre-
dicted increase in metabolism in the tropics was large, despite the small
rise in temperature there (Fig. 1a), because tropical warmingtook place
in an environment that was initially warm.
Absolute changes in metabolic rates determine an organism’s total
energy use and thus the impacts of climate change on ecosystem-level
processes, but per cent changes in metabolic rates are nonetheless
relevant to the impacts of climate change on individual organisms
22
.
Such relative changes in metabolic rates (expressed as per cent of the
standard reference period on a per-station basis) closely match tem-
perature changes (Fig. 1c), indicating that impacts on individual
ectotherms have probably been relatively large in the Arctic and north
temperate zones.
To evaluate whether the patterns described earlier (Fig. 1b) are robust
to our use of average values of Eand b
0
, we re-ran analyses using esti-
mates of Eand b
0
specific to diverse ectotherm taxa (Supplementary
Table 1)
12
. Large effects of recent climate warming on metabolic rates
are predicted for invertebrates, amphibians and reptiles in equatorial
1
Department of Zoology and Physiology, University of Wyoming, Laramie, Wyoming 82071, USA.
2
Department of Biology, Box 351800, University of Washington, Seattle, Washington 98195, USA. {Present
address: Max Planck Institute for Developmental Biology, Tu
¨bingen 72076, Germany.
704 | NATURE | VOL 467 | 7 OCTOBER 2010
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©2010
West Africa, the Caribbean and Central America, Ecuador, eastern
equatorial Brazil, and the Persian Gulf region (Fig. 2c–e). However, we
emphasize that weather station coverage in some of these regions is
sparse and each taxonomic group is not found in all geogr aphical regions.
Overall, general patterns in Fig. 1bare robust for different taxa (Fig. 2b–e):
the largest predicted absolute shifts in metabolic rate for all taxa are in
the tropics. Nevertheless, small differences in the relationship between
metabolism and temperature (that is, Eand b
0
) can alter the magnitude
of the effects of climate warming on organism physiology (Fig. 2).
The patterns under discussion are for mass-normalized metabolic
rates, but the magnitude of metabolic shift will necessarily differ for small
versus large ectotherms. Of course, absolute shifts will be greater for larger
ectotherms, but equation (1) indicates that mass-specific metabolic rates
of small ectotherms will show larger increases (Supplementary Fig. 3).
Several assumptions underlie the patterns shown in Fig. 1b, c. The
exponent (3/4) for metabolic rate as a function of mass is debated
16–18
,
but reasonable shifts of this exponent for given taxa will only alter the
heights of all latitudinal lines, not their relative ordering. We assume
that surface air temperatures approximate ectotherm body tempera-
tures; therefore, our metabolic estimates apply to thermoconforming
and exposed ectotherms. This is reasonable for small ectotherms living
in shaded environments
23
, but less so for large ectotherms that live in
thermally heterogeneous environments, where behavioural thermo-
regulation is possible, or for organisms that spend extensive periods
in retreats
24
. Also, we assume that the coefficients (E,b
0
) of equation
(1) are independentof latitude.However, somehigh-latitude ectotherms
have relatively elevated metabolic rates; and this is thought to represent
an evolutionary metabolic compensation for the physiologically depres-
sing effects of low body temperature
16,25,26
. With reference to equation
(1), metabolic compensation would be indicated
26
by latitudinal
increases in b
0
and/or in E. In fact, the patterns of metabolic responses
shown in Fig. 1b hold even when we shift these parameters over a large
−0.5
0
0.5
1.0
1.5
2.0
1980 1990 2000 2010
a
Change in temperature (°C)
Tropical
North temperate
South temperate
Arctic
Tropical
North temperate
South temperate
Arctic
Tropical
North temperate
South temperate
Arctic
−0.01
0
0.01
0.02
0.03
0.04
0.05
1980 1990 2000 2010
b
Change in metabolic rate (mW g–3/4)
YearYear Year
−5
0
5
10
15
20
25
1980 1990 2000 2010
c
Change in metabolic rate (%)
Figure 1
|
Global changes in temperature and in metabolic rates since 1980.
a, Changes in mean temperature (5-year averages) for Arctic (n5100 grid
cells), north temperate (n5356), south temperate (n551) and tropical
(n5169) regions. b, Predicted absolute changes in mass-normalized metabolic
rates by geographical region. c, Predicted relative changes in mass-normalized
metabolic rates. Both temperature and metabolic rate are expressed as
differences from the standard reference period (1961–1990), calculated on a
per-station basis, on the basis of Eand b
0
for an average ectotherm
(Supplementary Table 1). Data points are means 6s.e.m. of area-corrected,
gridded weather-station data (Methods).
60° S
30° S
30° N
60° N
60° N
60° N 60° N
60° N
180° W
120° W
60° W
60° E
120° E
180° E
60° S
30° S
30° N
180° W
120° W
60° W
60° E
120° E
180° E
60° S
30° S
30° N
180° W
120° W
60° W
60° E
120° E
180° E
60° S
30° S
30° N
180° W
120° W
60° W
60° E
120° E
180° E
60° S
30° S
30° N
180° W
120° W
60° W
60° E
120° E
180° E
aChange in temperature
−1.4 °C
3.4 °C
b
Change in metabolic rate
Unicellular organisms
−0.08
mW g−3/4
0.15
mW g−3/4
cInvertebrates
dAmphibians eReptiles
Figure 2
|
Predicted changes in metabolic rates
of diverse terrestrial ectotherms. a, Difference in
temperature between 1961–1990 and 2005–2009,
with scale bar shown on right. be, Difference in
mass-normalized metabolic rates (predicted) for
the same period for four terrestrial ectothermic
animal taxa for which empirical estimates of Eand
b
0
are available (Supplementary Table 1)
12
. Colour
bar to right of bindicates scale for be. Grey
shading indicates grid cells with no temperature
data.
LETTER RESEARCH
7 OCTOBER 2010 | VOL 467 | NATURE | 705
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range of biologically reasonable values
26
to simulate extreme metabolic
compensation at high latitude (Methods and Supplementary Fig. 4).
Our analyses indicate that warming during the past three decades has
had its biggest absolute impacts on metabolic rates in tropical and north
temperate zones (Fig. 1b). The outlook for future warming is less clear.
Without predictions of future daily and seasonal temperature cycles (not
merely of mean annual temperatures), we cannot directly estimate
future metabolic changes without violating the fallacy of averages
15
.
Nevertheless, our analyses of recent temperature data indicate that even
when the temperature shifts in the north temperate region are more than
double those in the tropics (Fig. 1a), absolute shifts in metabolic rates are
similar in the two regions (Fig. 1b). If this pattern holds, projected
increases in median surface air temperature by the end of the twenty-
first century for the two regions (3.5–4.0 uC in the tropics,and 4.0–5.5 uC
in the north temperate zone)
8
should cause roughly similar absolute
increases in metabolic rates of tropical and north temperate organisms.
Recent studies using diverse physiological and biophysical ap-
proaches indicate that tropical ectotherms may be particularly vulner-
able to climate warming
2,7,13,14,24,27
, even though observed and predicted
tropical warming is relatively small
8
. Our estimates suggest that tropical
ectotherms are also experiencing large increases in metabolic rate (Fig.
1b). Such increases will have physiological and ecological impacts:
warmed tropical ectotherms will have an increased need for food and
increased vulnerability to starvation unless food resources increase,
possible reduced discretionary energy for reproduction
22
, increased
rates of evaporative water loss in dry environments and altered demo-
graphies
13
. Larger increases in metabolic rates of tropical soil biota
may explain larger absolute changes in tropical soil respiration
28
.
Furthermore, metabolic increases should alter food web dynamics,
leading to elevated rates of herbivory and predation, as well as changes
in the spread of insect-borne tropical diseases
29
. Because the tropics are
the centre of Earth’s biodiversity and its chief engine of primary pro-
ductivity, the relatively large effects of temperature change on the meta-
bolism of tropical ectotherms may have profound local and global
consequences.
METHODS SUMMARY
We obtained hourly temperature records from 22,486 weather stations spread
across the world
20
, but then included only stations that sampled throughout the
IPCC standard reference period (1961–1990)
8
as well as 1991–2009, in all seasons
and on average at leastevery six hours.We also excludedfive Antarcticstations,such
that 3,186 stations remained. Geographical coverage is uneven (Supplementary
Fig. 1), but all regions are well represented in this restricted data set (Supplemen-
tary Table 2). Furthermore, including data from 5,561 stations with data from 1961
to 2009 (but with no other limitations; Supplementary Table 2), does not alter our
conclusions (Supplementary Fig.5). To correct for the unevenspatial distribution of
stations (Supplementary Figs 1 and 5A), we computed mean temperatures and
metabolicrates for all stations within 5ulatitude by 5ulongitude cells. We calculated
means and standard errors for latitudinal regions by weighting grid-cell means by
the interpolated rectangular mid-cell areas
30
. To estimate whether metabolic com-
pensation at high latitude might alter patterns,we recalculated metabolic rates after
substituting extreme values of Eand of b
0
. Specifically, we used veryhigh values of E
(0.76)and b
0
(26.85)for the north temperate and Arctic areas,but very low valuesof
E(0.50) andb
0
(15.68)for tropical areas(see Supplementary Table 1). Such extreme
metabolic compensation (these values span most of the known range of E)
26
does
not alter our conclusions (Supplementary Fig. 4).
Full Methods and any associated references are available in the online version of
the paper at www.nature.com/nature.
Received 5 June; accepted 10 August 2010.
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Supplementary Information is linked to the online version of the paper at
www.nature.com/nature.
Acknowledgements We thank T. L. Daniel, C. Martı
´nez del Rio, W. R. Rice and J.
Tewksbury for discussion, and S. L. Chown for sharing his data on latitudinal variation
in E. Researchwas funded in part by NSF IOB-041684 to R.B.H. andby an NSF Minority
Postdoctoral Fellowship to M.E.D.
Author Contributions M.E.D., G.W. and R.B.H. conceived the project, designed the
analyses and wrote the paper; M.E.D. and G.W. collated weather station data and did
temperature and metabolic rate calculations.
Author Information Reprints and permissions information is available at
www.nature.com/reprints. The authors declare no competing financial interests.
Readers are welcome to comment on the online version of this article at
www.nature.com/nature. Correspondence and requests for materials should be
addressed to M.E.D. (Michael.Dillon@uwyo.edu).
RESEARCH LETTER
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METHODS
Weather station data. We downloaded all available ‘isd-lite’ weather-station data
(http://www.ncdc.noaa.gov/oa/climate/isd/index.php)
20
. From the initial 22,486
weather stations, we extracted a ‘restricted’ data set (3,186 stations) that sampled
throughout the entire IPCC standard reference period (1961–1990)
8
as well as up
to 31 December 2009, in all seasons, and at least every six hours. (We did not
include Antarctic stations.) This data set had a total of 493,256,415 temperature
measurements with an average of 8.8 temperature measurements per station per
day; it was used for Figs 1 and 2 and Supplementary Figs 1–4. For the ‘unrestricted’
data set, we included all stations (other than Antarctic) that had data for the above
time period, independentof the seasonality or frequency of sampling. This data set
had 5,561 stations (used for Supplementary Fig. 5).
Metabolic rate estimates. To estimate metabolic rates from temperature data, we
used empirically derived estimates of the coefficients (Eand b
0
) of the equation
relating metabolic rate to temperature and body mass for unicellular organisms,
multicellular invertebrates, amphibians and reptiles
12
. We excluded fish because
our data are air (not water) temperatures. We excluded birds and mammals
because their body temperatures will not match air temperatures. We excluded
plants because the temperature dependence of their metabolic rates differs fun-
damentally from that of animal ectotherms
31
.
Mean temperatures are expedient for analyses of the impacts of climate warm-
ing. However, because the relationship between temperature and metabolicrates is
inherently nonlinear, the use of mean rather than individual temperatures to
predict metabolic rates will induce spurious results
32
—an effect known as the
‘fallacy of the averages’
15
. To illustrate this fallacy, we recomputed metabolic rates
for geographical regions using mean annual temperatures (Supplementary Fig. 2)
for comparison with rates predicted from ‘instantaneous’ temperatures (Fig. 1b).
Note that the use of mean temperatures underestimates the predictedincreases in
metabolic rates
15
, and also de-emphasizes the impact of warming in the north
temperate zones relative to the tropics. Consequently, it is imperative to use high-
frequency temperature data and to compute metabolic rate separately for each
temperature measurement.
Our analysis includes temperatures that fall outside the normal tolerance range
of most organisms (that is, below ,0uC and above ,40 uC). We include these
values for analytical transparency, and because their inclusion is conservative for
our analyses. Eliminating negative temperatures (for example, substituting meta-
bolic rates at 0 uC for all temperatures below 0 uC) will have little effect because
metabolic rates are negligible at these extremely cold temperatures. Substituting
metabolic ratesat 40 uC for temperatures above 40 uCwill tend to reduce metabolic
rates at mid-latitudes where these hot temperatures occur in summer; this would
induce a downward bias in our predicted metabolic rates for the north temperate
zone. In other words, by not truncating metabolic rates to the normal tolerance
range (0–40 uC), we avoid a bias that would favourincreased metabolic rates in the
tropics.
Geographical coverage. Weather stations are not equally spaced across the world
(summarized in Supplementary Table 2, Supplementary Figs 1 and 5a). To adjust
for the uneven spatial distribution (and non-independence) of stations, we com-
puted mean temperatures and metabolic rates for all stations within 5ulatitude by
5ulongitude grid cells (see Fig. 2). We then calculated means and standard errors
for latitudinal regions (see Fig. 1) by weighting grid-cell means by interpolated
rectangular mid-cell areas
30
. We further tested the effects of weather station spatial
coverage on our conclusions by comparing analyses using restricted (3,186 sta-
tions) and unrestricted (5,561 stations) data sets. Our conclusions are robust and
independent of the data set used (Supplementary Fig. 5).
Assumptions. We assume that station temperatures match the temperature of a dry-
skinned ectotherm positioned in shade at 2-m height. Of course, mobile ectotherms
can often use behaviour (for example, microhabitat selection) to buffer body tem-
peratures against changes in air temperatures
23,24
. Thus our metabolic estimates
should be viewed as an estimate for a non-regulating, inert and exposed ectotherm.
We assume that a singlemetabolic curve (equation (1))applies to all ectotherms,
independent of latitude. However, some high-latitude ectotherms have relatively
raised metabolic rates, which may reflect metabolic compensation for temper-
ature
26
. To estimate whether metabolic compensation at high latitude might alter
latitudinal patterns (Fig. 1), we recalculated metabolic rates after substituting
extreme values of Eand b
0
. Specifically, we used very high values of E(0.76) and
b
0
(26.85) for the north temperate and Arctic areas, but very low E(0.50) and b
0
(15.68) for tropical areas (see Supplementary Table 1). Such extreme metabolic
compensation(these values span most of the known range of E)
26
does not alter our
conclusions (Supplementary Fig. 4).
Statistics. We used an ordered-heterogeneity test
21
to evaluate whether latitudinal
ordering of changes in temperature since 1980 predicts the latitudinal ordering of
changes in metabolic rate.
31. Reich, P. B., Tjoelker, M. G., Machado, J.-L. & Oleksyn, J. Universal scaling of
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... Furthermore, few studies have explored the potential benefits of multi-species management strategies compared to single-species approaches in promoting network persistence under different climate scenarios 23 . These limitations lead to considerable uncertainty regarding the effectiveness of current 'universal' management strategies for sustaining ecosystems around the globe, particularly since species' thermal properties vary across regions 24 . ...
... Tropical species often operate close to their thermal limits 17 , making them more susceptible to even slight increases in temperature, while temperate regions typically remain below these critical thresholds, exhibiting less extreme responses to warming 17,20,24 . Such interspecific variability suggests that active management may produce different outcomes depending on the region. ...
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Anthropogenic warming impacts ecological communities and disturbs species interactions, particularly in temperature sensitive plant pollinator networks. While previous assessments indicate that rising mean temperatures and shifting temporal variability universally elevate pollinator extinction risk, many studies often overlook how plant-pollinator networks of different ecoregions require distinct management approaches. Here, we integrate monthly near-surface temperature projections from various Shared Socioeconomic Pathways of CMIP6 Earth System Models with region-specific thermal performance parameters to simulate population dynamics in 11 plant pollinator networks across tropical, temperate, and Mediterranean ecosystems. Our results show that tropical networks, already near their thermal limits, face pronounced (50 percent) pollinator declines under high-emissions scenarios (SSP5-8.5). Multi-species management targeting keystone plants emerges as a critical strategy for stabilizing these high risk tropical systems, boosting both pollinator abundance and evenness. In contrast, temperate networks remain well below critical temperature thresholds, with minimal (5 percent) pollinator declines and negligible gains from any intensive management strategy. These findings challenge single-species models and uniform-parameter frameworks, which consistently underestimate tropical vulnerability while overestimating temperate risk. We demonstrate that explicitly incorporating complex network interactions, region-specific thermal tolerances, and targeted multi species interventions is vital for maintaining pollination services. By revealing when and where limited interventions suffice versus extensive management becomes indispensable, our study provides a clear blueprint for adaptive, ecosystem specific management under accelerating climate change.
... To do this, we analyzed the time data using linear models with the nlme package. In time series studies focused on determining the ecological impacts of shifting average environmental conditions in shaping the structure and functioning of ecosystems under climate change (i.e., community dynamics), it is crucial to consider and quantify the temporal structure or autocorrelation of environmental variables [125][126][127] . This is because autocorrelation is simply defined by the correlation of adjacent time points, where its negative effects have been well-established regardless of the model and system 128 . ...
... First, the temporal trend of the selected climate variables was studied with linear generalized least squares regression 129 (GLS), using the gls function in the nlme package. GLS regression is a classical method for quantifying time trends because, unlike ordinary linear regression models, it allows to correct estimate model variance and quantify heteroscedasticity and autocorrelation of residuals in the temporal climate data 125,130 . GLS was run separately on each selected climate variable (i.e., T, P, ΔT, ΔP, SPEI and NSCD), where model agreement and robustness of trends were statistically assessed following the GLS fits 129 . ...
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There is a significant lack of research on how climate change influences long-term temporal trends in the biodiversity of soil organisms. Nematodes may be specifically adequate to test soil biodiversity changes, because they account for ~80% of all Metazoans and play key roles in the functioning of terrestrial ecosystems. Here, we report on the first synthesis study focused on temporal trends of nematode fauna over a period of 14 years (1986–1999) across the Carpathian Ecoregion. We provide new evidence that wetter conditions associated to global change contributes to driving nematode diversity at genus/family level. We observed opposite trends in soil nematode alpha diversity (increase) and beta diversity (decrease) consistent across ecosystem types and soil horizons, providing strong evidence for the influence of climate change on soil biodiversity at large spatial scales. An increase in the community functional uniformity along with a decline in beta diversity indicated more homogenous soil conditions over time. The Soil Stability Index (metric devised to assess soil homeostasis based on the functional composition of nematode communities) increased over time, indicating a decline of soil disturbances and more complex soil food webs. Our results highlight the importance of nematodes as powerful indicators of soil biodiversity trends affected by multiple facets of environmental change in long-term soil monitoring.
... Other testing reported that an 18-h exposure to endosulfan and increasing ambient temperatures did not have a statistically significant effect on gill ventilation frequency of silver perch, although the short exposure duration complicates interpretation 153 . Comparative analyses of differing thermal regimes have also suggested that tropical marine ectotherms may be more susceptible to climate warming given their elevated baseline body temperature and narrower thermal safety margins [154][155][156][157] . However, the role of POP exposures in affecting responses of tropical marine biota to climate warming remains unstudied. ...
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Understanding climate change impacts in combination with other anthropogenic stressors, such as chemical pollution, is critical to identifying vulnerable marine ecosystems. This paper presents a systematic review and conceptual model mapping evidence of the marine environmental fate and biological effects of persistent organic pollutants with shifting climate drivers. Increasing ice melt, atmospheric deposition, and sediment remobilization are altering persistent organic pollutant dynamics in northern polar environments, but with data gaps elsewhere. While limited to fish and invertebrates, principal biological effect pathways involve reduced survival and perturbed thermal regulation and bioenergetics, notably in some populations residing in more heavily polluted and thermal edge habitats. Associated food web shifts with climate change are also altering persistent organic pollutant bioaccumulation among some marine mammal and seabird populations and assemblages. The evidence suggests potential ecological deterioration in some areas, with many unknowns underscoring the need for advancing experimental and modeling tools to evaluate these complex interactions.
... Increased temperatures and altered rainfall patterns have been predicted by several climate forecasting models, with greater effects in the region [12,39]. For several decades, the yield in many places in Africa was projected to decline by 25% for every degree increase in the mean surface temperature [25]. According to Schlenke rand Lobel [99], the addition of 2 °C of warm temperature was predicted to induce crop losses of approximately 27% to 32%. ...
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Climate change is the key factor that influences food security in Africa. Essentially, it has contributed to a great increase in drought stress, flooding, salinity, land degradation, sliding and soil erosion. Because of the effect of climate change, plant pests and diseases have also become another significant obstacle to the agricultural development in Africa. Consequently, Africa's food production and supply system is becoming increasingly vulnerable to climate change. As such, Africa needs to opt for new ways to support their traditional breeding methods - the majority of which are no longer effective to handle and overcome the climatic challenges. The genome editing technology has become more useful in agriculture, especially after the recent discovery of the Clustered Regularly Interspaced Short Palindromic Repeats-associated endonuclease Cas9 (CRISPR-Cas9) system. Because of its simplicity, efficiency, and specificity, CRISPR-Cas9 has moved far beyond genetically modified (GM) technology to solve biotic and abiotic challenges, especially in developed countries. Through this technique, a variety of crops now produce site-specific alterations useful in crop production improvement. Several credible studies have brought out some encouraging results regarding the potential of this technique to address climate change in crop production. Despite its advantages in overcoming drought stress, salinity, flooding, pest and disease challenges in some developed countries, Africa is lagging behind in adopting and exploiting it effectively. It is a very small number of African nations that embrace and apply this technique to solve their climate-induced challenges in crop production. Technical, infrastructure, regulatory, policy and socio-economic factors are the primary causes of Africa's limited adoption of this technology. In order to accommodate this technology sufficiently, the African nations must improve their infrastructure and knowledge base while updating their policies and legal framework on gene editing. Finally, they ought to improve the capacity building and collaboration with nations possessing the technology to incorporate it into their food security strategies.
... Hypometabolism during winter dormancy is sustained by low winter temperatures that lower metabolic rate via the Q 10 effect Denlinger, 2007, 2011). For temperate species of insects, metabolic rates drop significantly while in diapause (Hoback and Stanley, 2001), but hotter temperatures may compromise this pattern by increasing metabolic rates (Angilletta, 2009;Dillon et al., 2010). Increased temperatures for both field and laboratory populations of diapausing Eurosta solidaginis larvae led to higher metabolic rates while in diapause, with decreased survival or decreased fecundity post-diapause (Hahn and Denlinger, 2007;Lee, 2000, 2003). ...
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As ectotherms, many insects spend the winter months in a state of suspended animation (i.e., diapause), lowering their metabolic rates to subsist on a limited store of energy reserves. The ability to lower metabolic rate during diapause relies, in part, on cold winter temperatures to intrinsically lower metabolic rate. Winter warming associated with global climate change may pose a challenge to diapausing insects by intrinsically increasing metabolic rate, potentially leading to the exhaustion of energetic reserves. We used stop-flow respirometry to measure oxygen consumption in response to temperatures representative of both acute and chronic winter warming scenarios in diapausing Pieris rapae pupae. Metabolic rate increased with increasing temperature in diapausing pupae, but metabolic rate depended on both pupal age and warming severity, with older pupae having lower metabolic rates overall. Despite the increases in metabolic rate, pupae recovered metabolic rate within 24-hours after short-term acute-warming exposure. In contrast, chronic exposure to warming over weeks and months led to significant decreases in metabolic rate later in diapause, as well as reductions in pupal mass. These results demonstrate that while respiration was thermally responsive, warming did not lead to sustained increases in metabolic rate. Instead, diapausing P. rapae appear to acclimate to higher temperature by lowering their metabolic rates in response to months of chronic warming. Overall, these patterns suggest that this species could be resilient to winter warming, at least in the context of energetics. However, the precise mechanisms underlying these responses remain to be characterized. Thus, future research—e.g., on the genetic underpinnings of energetics in the context of warming—could further elucidate the relative vulnerability of diapausing insects to future winter warming.
... as insects (Chown et al., 2011;Dillon et al., 2010;Sinclair et al., 2024;Wigglesworth, 1986;Woods & Smith, 2010), and both dry spells and heat waves would co-occur more frequently in a warmer climate (Sarhadi et al., 2018). These combined stressors can trigger range shifts that are larger and faster than would be expected by warming alone (Kearney et al., 2018). ...
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By increasing the mean and variance of environmental temperatures, climate change has caused local extinctions and range shifts that are likely to intensify over time. Previously, biologists projected impacts of climate change from the acute heat tolerances of adult organisms; however, this approach ignores important factors, such as the cumulative damage from heat exposure and the variation in heat tolerance among individuals in different physical conditions and at different life stages. We measured the effects of hydration state and life stage on the heat tolerance of an agricultural pest, the South American locust (Schistocerca cancellata). By measuring tolerance time across a range of temperatures, we estimated tolerance of both chronic and acute exposures to high temperatures. We then used these data to model the injury and survival of locusts in microclimates of the past (1961–1990), present (1991–2020) and future (uniform warming of 3°C). Locusts succumbed to heat stress exponentially faster as temperature increased, but hydration state and life stage altered this exponential relationship. Our modelling indicated that recent climate change has amplified the risk of overheating, with predicted injury and survival depending strongly on a locust's access to shade and water. If changes in climate and land use reduce the availability of these resources, locust populations may shift their geographic range faster than currently predicted. To accurately predict range shifts and associated crop losses, mechanistic models of locust distributions should consider the combined stressors of heat and dehydration. Read the free Plain Language Summary for this article on the Journal blog.
... Because tropical climates are less variable and tropical organisms are adapted to almost same temperature ranges than are temperate and arctic species which are more sensitive to slight climate changes (Deutsch, 2008). And also because of metabolic rate increases when temperature increases and organisms in the tropics adapted to a greater change in metabolism with increasing temperature than organisms in temperate and Polar Regions (Dillon, 2010). Actually when we see both recent global warming and the relationship between metabolic rate and temperature, organisms in tropical and northern temperate zones are experiencing the largest increase in metabolic rates. ...
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Small mammals are one of the most successful and diverse groups of mammals which inhabit a wide range of habitats in different area of the world, and most of them are rodents. Small mammals with their arthropod ectoparasites which live near to human's inha transmission of diseases to humans and domestic animals. The transmission of pathogens to humans is influenced by climatic variability such as, flooding, change in rainfall pattern and increase in temperature which m displaced from their natural habitats. As a result, bring them into closer contact with humans and domestic animals which increase potential zoonotic disease transmission. Moreover, c may also result changes in human lifestyles, such as an increase in outdoor activities which increase human small mammals reservoirs. Therefore, ident health concern in response to climate change will enable us to deploy better and more accurate management strategies against zoonotic disease spread.
... It is indigenous to the tropical-subtropical regions in the Western Hemisphere, although its distribution has expanded over large parts of America, Africa, Asia and Oceania in the last few years. Global climate change may significantly impact the geographic distribution of biodiversity, alter biodiversity, and affect interactions between species and ecosystems [1]. Temperature is one of the abiotic factors that exerts great influence on insect biology and this factor can affect the duration of the life cycle, population density, size and genetic composition, the extent of host plant exploitation, as well as local and geographic distribution linked to colonization and extinction [2]. ...
Article
The problem of increasing salinity and mineralization in natural and artificial freshwater bodies with climate warming is very relevant nowadays, as it leads to changes in the species composition of planktonic organisms. Testate amoebae are one of the responsive bioindicators that are sensitive to even minor changes in environmental conditions. In this study, a comparative analysis of the species diversity of planktonic testate amoebae was carried out in a number of lakes in the forest–steppe and forest–swamp natural zones of Western Siberia using microscopy and metabarcoding. One new species, Pseudodifflugia siemensmai sp. nov., was described. The detection frequency and the number of reads of amplicon sequence variants of potentially pathogenic testate amoebae belonging to the genera Rhogostoma and Fisculla were higher in forest–steppe lakes. Universal eukaryotic primers for the 18S rRNA gene are well suited for identifying testate amoebae from the supergroup Cercozoa but are practically not applicable for identifying Amoebozoa testaceans. The plankton of the lakes with the highest mineralization and salinity was characterized by the most specific species composition. These results should be taken into account when predicting changes in aquatic communities with further climate warming, which may also be associated with an increase in the occurrence of pathogenic testaceans that pose biosafety threats. IMPORTANCE Microscopic and metabarcoding analyses reveal important differences in testate amoebae communities in lakes in two natural and climatic zones of Western Siberia that should be taken into account when predicting changes in aquatic communities with further climate warming, which may also be associated with an increase in the occurrence of pathogenic testaceans that pose biosafety threats.
Article
Isoprene, emitted by some plants, deters insect herbivory. However, the associated biochemical and physiological responses that confer herbivory resistance remain unknown. We used engineered isoprene-emitting (IE) and non-emitting (NE) control tobacco plants to interpret isoprene-mediated defense against herbivory in plants. Hornworm larvae raised on IE plants exhibited stunted growth compared to those raised on NE plants. Worms preferred to feed on NE rather than IE leaves, indicating deterrent effects of isoprene on insect feeding. Worm feeding induced a greater increase in jasmonic acid (JA), a crucial hormone for insect resistance, in IE leaves compared to that in NE leaves. Assimilation rates were stably maintained in IE plants, suggesting a protective role of isoprene in preserving photosynthetic efficiency during insect herbivory. Wound-induced increase in isoprene emission correlated with the elevation of key metabolites of the isoprene biosynthesis pathway. Our results highlight JA-priming functions of isoprene and provide insights into isoprene-mediated defense against insect herbivory.
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The impact of anthropogenic climate change on terrestrial organisms is often predicted to increase with latitude, in parallel with the rate of warming. Yet the biological impact of rising temperatures also depends on the physiological sensitivity of organisms to temperature change. We integrate empirical fitness curves describing the thermal tolerance of terrestrial insects from around the world with the projected geographic distribution of climate change for the next century to estimate the direct impact of warming on insect fitness across latitude. The results show that warming in the tropics, although relatively small in magnitude, is likely to have the most deleterious consequences because tropical insects are relatively sensitive to temperature change and are currently living very close to their optimal temperature. In contrast, species at higher latitudes have broader thermal tolerance and are living in climates that are currently cooler than their physiological optima, so that warming may even enhance their fitness. Available thermal tolerance data for several vertebrate taxa exhibit similar patterns, suggesting that these results are general for terrestrial ectotherms. Our analyses imply that, in the absence of ameliorating factors such as migration and adaptation, the greatest extinction risks from global warming may be in the tropics, where biological diversity is also greatest. • biodiversity • fitness • global warming • physiology • tropical
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It is predicted that climate change will cause species extinctions and distributional shifts in coming decades, but data to validate these predictions are relatively scarce. Here, we compare recent and historical surveys for 48 Mexican lizard species at 200 sites. Since 1975, 12% of local populations have gone extinct. We verified physiological models of extinction risk with observed local extinctions and extended projections worldwide. Since 1975, we estimate that 4% of local populations have gone extinct worldwide, but by 2080 local extinctions are projected to reach 39% worldwide, and species extinctions may reach 20%. Global extinction projections were validated with local extinctions observed from 1975 to 2009 for regional biotas on four other continents, suggesting that lizards have already crossed a threshold for extinctions caused by climate change.
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Significant changes in physical and biological systems are occurring on all continents and in most oceans, with a concentration of available data in Europe and North America. Most of these changes are in the direction expected with warming temperature. Here we show that these changes in natural systems since at least 1970 are occurring in regions of observed temperature increases, and that these temperature increases at continental scales cannot be explained by natural climate variations alone. Given the conclusions from the Intergovernmental Panel on Climate Change (IPCC) Fourth Assessment Report that most of the observed increase in global average temperatures since the mid-twentieth century is very likely to be due to the observed increase in anthropogenic greenhouse gas concentrations, and furthermore that it is likely that there has been significant anthropogenic warming over the past 50 years averaged over each continent except Antarctica, we conclude that anthropogenic climate change is having a significant impact on physical and biological systems globally and in some continents.
Article
Recent warming has caused changes in species distribution and abundance, but the extent of the effects is unclear. Here we investigate whether such changes in highland forests at Monteverde, Costa Rica, are related to the increase in air temperatures that followed a step-like warming of tropical oceans in 1976 (refs4, 5). Twenty of 50 species of anurans (frogs and toads) in a 30-km2 study area, including the locally endemic golden toad (Bufo periglenes), disappeared following synchronous population crashes in 1987 (refs 6-8). Our results indicate that these crashes probably belong to a constellation of demographic changes that have altered communities of birds, reptiles and amphibians in the area and are linked to recent warming. The changes are all associated with patterns of dry-season mist frequency, which is negatively correlated with sea surface temperatures in the equatorial Pacific and has declined dramatically since the mid-1970s. The biological and climatic patterns suggest that atmospheric warming has raised the average altitude at the base of the orographic cloud bank, as predicted by the lifting-cloud-base hypothesis,.
Article
1. How body mass and body temperature influence metabolic rate has been of interest for decades. Today that interest can be seen in the form of debates over the proper scaling coefficients, and the mechanistic underpinnings of allometric models for metabolic rate in relation to body mass and body temperature. We tested explicit assumptions built into what we term the Arrhenius fractal supply (AFS) model of these relationships. This model, and its assumptions, is foundational to the controversial Metabolic Theory of Ecology. 2. In addition to predicting that the scaling exponent for body mass is 3/4, the AFS model originally predicted that metabolic responses to body temperature, measured as activation energies, should fall between 0·2 and 1·2 eV. More recently, the latter range was narrowed to 0·6 and 0·7 eV. 3. To test the AFS’s predictions, we used multiple regression of ln(metabolic rate) as a function of ln(body mass) and 1/(body temperature) to fit the best scaling exponent for body mass to nine data sets of many diverse species. 4. For the majority of the data sets, in addition to not supporting a scaling exponent of 3/4, the analyses indicated that effects of body temperature sometimes fell outside the range of 0·6–0·7 eV, indicating that the predictions of the AFS model do not hold universally. 5. Effects of body temperature, however, did fall within the range of 0·2–1·2 eV. To aid interpretation of these results, we transformed activation energies into Q10s. At ecologically realistic temperatures, the values of Q10 that approximate activation energies of 0·2–1·2 eV ranged from c. 1·4 to 6·1 (where 6·1 is clearly unreasonably high). Hence, any model that predicts activation energies between 0·2 and 1·2 eV does not appear to be an informative scaling model at the organismal level. 6. The AFS model is foundational for the Metabolic Theory of Ecology. While we commend the attempt to incorporate scaling of metabolism into ecological theory, and the research it has inspired, we caution against using untested, and likely incorrect, assumptions as a foundation to a general theory of ecology. We recommend that scientists allow the data to determine the best model for incorporating energetics into ecological theory.
Article
Many biologists now recognize that environmental variance can exert important effects on patterns and processes in nature that are independent of average conditions. Jensen’s inequality is a mathematical proof that is seldom mentioned in the ecological literature but which provides a powerful tool for predicting some direct effects of environmental variance in biological systems. Qualitative predictions can be derived from the form of the relevant response functions (accelerating versus decelerating). Knowledge of the frequency distribution (especially the variance) of the driving variables allows quantitative estimates of the effects. Jensen’s inequality has relevance in every field of biology that includes nonlinear processes.